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| sector:waste:biological_treatment_solid_waste_disposal:start [2025/10/20 11:08] – [Recalculations] schiller | sector:waste:biological_treatment_solid_waste_disposal:start [2026/03/16 14:19] (current) – [Table] mielke | ||
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| Line 9: | Line 9: | ||
| ---- | ---- | ||
| - | | NO< | + | | NO< |
| - | | NA | + | | NA |
| - | | {{page> | + | | {{page> |
| In category **5.A**, __NMVOC and PM< | In category **5.A**, __NMVOC and PM< | ||
| Line 24: | Line 24: | ||
| ===== Methodology ===== | ===== Methodology ===== | ||
| - | For the estimation of NMVOC, Germany decided against the proposed EF of the EMEP/EEA Guidebook | + | For the estimation of NMVOC, Germany decided against the proposed EF of the EMEP/EEA Guidebook |
| According to national experts in the field, the approach of the US-EPA is more likely to produce better data, because the ratio between NMVOC (1.3 %) and CH< | According to national experts in the field, the approach of the US-EPA is more likely to produce better data, because the ratio between NMVOC (1.3 %) and CH< | ||
| - | Emissions for PM< | + | Emissions for PM< |
| The EFs are multiplied with the total amount of solid waste (AD) treated in managed above-ground landfills, following the standard equation: | The EFs are multiplied with the total amount of solid waste (AD) treated in managed above-ground landfills, following the standard equation: | ||
| Line 49: | Line 49: | ||
| ===== Uncertainties ===== | ===== Uncertainties ===== | ||
| - | The AD from Statistisches Bundesamt usually have an uncertainty of ±3% whereas the uncertainties for the PMs and TSP emission factors, according to the EMEP/EEA Guidebook (Part B, 5.A, chap. 3.2.2, Table 3-1, p. 5), were estimated as: | + | The AD from Statistisches Bundesamt usually have an uncertainty of ±3% whereas the uncertainties for the PMs and TSP emission factors, according to the EMEP/EEA Guidebook (Part B, 5.A, chap. 3.2.2, Table 3-1, p. 6), were estimated as: |
| __Table 1: Uncertainty estimates of PM emission factors__ | __Table 1: Uncertainty estimates of PM emission factors__ | ||
| Line 64: | Line 64: | ||
| However, in this year's reporting the correction of the deposited waste quantities is higher than usual and thus is affecting the recalculation of TSP an PMs to a higher extend than is usually the case. For this reason, the recalculation is reported here. For the sake of completeness NMVOC emissions are also reported.\\ | However, in this year's reporting the correction of the deposited waste quantities is higher than usual and thus is affecting the recalculation of TSP an PMs to a higher extend than is usually the case. For this reason, the recalculation is reported here. For the sake of completeness NMVOC emissions are also reported.\\ | ||
| - | __Table 1: Revised NMVOC-emissions [kt]__ | + | __Table 1: Revised |
| - | | ^ 2023 ^ | + | |
| ^ current submission | ^ current submission | ||
| - | ^ previous submission | + | ^ previous submission |
| + | \\ | ||
| __Table 2: Revised 2023 PM and TSP emissions, in [t]__ | __Table 2: Revised 2023 PM and TSP emissions, in [t]__ | ||
| - | | ^ TSP ^ PM< | + | | ^ TSP |
| - | ^ current submission | + | ^ current submission |
| - | ^ previous submission | + | ^ previous submission |
| <WRAP center round info 60%> | <WRAP center round info 60%> | ||
| - | For **pollutant-specific information on recalculated emission estimates for Base Year and current year**, please see the recalculation tables following [[general: | + | For **pollutant-specific information on recalculated emission estimates for Base Year and 2023**, please see the recalculation tables following [[general: |
| </ | </ | ||
| Line 88: | Line 88: | ||
| - | [(DESTATIS2024> | + | [(DESTATIS2024> |
| - | [(EMEPEEA2019> | + | [(EMEPEEA2023> |
| - | [(STEGMANN2018> | + | https:// |
| - | Ingenieurgruppe RUK GmbH, Stuttgar): Überprüfung der methodischen Grundlagen zur Bestimmung der Methanbildung in Deponien, ISSN 1862-4804; https:// | + | [(EMEPEEA2019> |
| + | [(STEGMANN2018> | ||